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Genetic Variation in Frost Tolerance, Early Height Growth, and Incidence of Forking Among and Within Provenances of Eucalyptus Fastigata

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Genetic Variation in Frost Tolerance, Early Height Growth, and Incidence of Forking Among and Within Provenances of Eucalyptus Fastigata 510 GENETIC VARIATION IN FROST TOLERANCE, EARLY HEIGHT GROWTH, AND INCIDENCE OF FORKING AMONG AND WITHIN PROVENANCES OF EUCALYPTUS FASTIGATA M. D. WILCOX Forest Research Institute, New Zealand Forest Service, Private Bag, Rotorua, New Zealand (Received for publication 7 April 1982; revision 21 July 1982) ABSTRACT One hundred and twenty-six seedlots (115 open-pollinated families and 11 composites) of Eucalyptus fastigata Deane & Maid, representing eight native provenances from New South Wales and Victoria, one exotic population from South Africa, and 15 exotic populations from New Zealand were planted in tests in 1979 at Kinleith and Kaingaroa, New Zealand. The trees were assessed at Kinleith in 1980 for height growth and tolerance to winter frosts, and at Kinleith and Kaingaroa in 1981 for incidence of forking. The seedlots varied greatly in frost tolerance, height growth, and incidence of forking. Components of variance for ''provenances" were 3 to 4 times larger than components for "families-in-provenance". The hardiest provenances gener­ ally grew the slowest and showed the lowest incidence of forking. By far the hardiest native provenances were from Oberon and Barrington Tops, New South Wales, confirming the outstanding frost-tolerance of these provenances recorded in artificial frosting tests. Families from New Zealand and from Robertson, New South Wales, were notably more frost-tender and more forked than those from other Australian localities, and from South Africa. New Zealand families from Oakura and Hunterville showed excellent vigour but generally poor frost- tolerance and a high frequency of forking. The provenance in which the families possessed the best combination of good frost-tolerance, fast growth, and freedom from forking was from Bondi State Forest (south of Bombala, New South Wales) towards the southern end of the species' natural range. The phenotypic correlations among family means within provenances were -0.41 between frost score and 1-year height (i.e., the tallest families generally showed the least frost damage), and 0.49 between 3-month and 1-year heights. Frost score at Kinleith was not well correlated at the family level (though highly correlated at the provenance level) with incidence of forking at either Kinleith itself or Kaingaroa. INTRODUCTION Eucalyptus fastigata is one of the ash group of eucalypts at present favoured in the North Island of New Zealand for growing as pulpwood and sawn timber. A genetic improvement programme was initiated in 1977 to breed strains with better stem and branching characteristics, and with adequate frost hardiness and vigour (Wilcox 1980). New Zealand Journal of Forestry Science 12(3): 510-24 (1982) Wilcox — Genetic variation in E. fastigata 511 Provenance variation in the frost tolerance of E. fastigata has been studied in some detail using artificial frosts (Wilcox, Rook & Holden 1980), and there have also been some studies reported of provenance variation in tolerance to natural frosts (Boden 1958; Roeder 1980; Sherry & Pryor 1967). A better impression of genetic variability within a species can be gained by examining variation among families from a range of provenances rather than looking at variation among composite provenance seedlots. In this paper genetic variation among and within several provenances of E. fastigata is measured and compared for three important silvicultural traits — early height growth, incidence of forking, and frost tolerance. The methods used are generally similar to those adopted for comparable studies on E. regnans F. Muell. (Wilcox, Faulds, Vincent & Poole 1980). MATERIALS AND METHODS Provenances and Families The genetic improvement programme for E. fastigata m New Zealand is based on 126 seedlots as listed in Table 1. Of these, 115 are open-pollinated families from individual mother trees and 11 are composite seedlots made up by bulking seed from several mother trees. Australian native stands are represented by 69 seedlots from eight provenances (Fig. 1), the parent trees of most of which can be regarded as random samples from the localities studied. The other 57 seedlots are from exotic stands in South Africa (six lots) and New Zealand (51 lots). Nearly all the New Zealand families are from carefully selected plus-trees showing good stem form and branching characteristics, and vigorous growth (Table 1). The New Zealand populations sampled (Fig. 2) ranged from small woodlots Dr plots of only 20 or so trees to extensive plantations of several hectares (e.g., Oakura and Hunterville). Most of the New Zealand seedlots were collected in 1977-78, and the Australian •ots were collected over the period 1966-77. Raising of Plants Seed was soaked in cold water for 24 hours, stratified for 8 weeks, and sown in August 1979. Germinants were pricked out at the cotyledon stage into 55 X 55-mm peat pots. The plants were started off in a glasshouse, and later transferred outside to grow on to plantable size. The seedlings were planted out in November 1979 when they had three fully formed pairs of opposite leaves and the first few alternate leaves, and mean heights of individual lots ranged from 6 to 19cm. The mean height of the five tallest trees per seedlot was recorded on 30 October 1979, 2 weeks before planting. Several families from the Hunterville provenance in particular had significant numbers of abnormal seedlings (e.g., crinkly leaves and yellow cotyledons). Such plants are presumably a consequence of self-fertilisation and were discarded. 512 New Zealand Journal of Forestry Science 12(3) TABLE 1—Origins of E. fastigata seedlots in New Zealand breeding programme Origin Lat. Long. Alt. Number of seedlots* (S) (E) (m) Families Composites New South Wales Barrington Tops 31° 50' 151° 20' 1370 7 1 Yetholme 33° 27' 149° 49' 1210 1 Oberon 33° 54' 149° 48' 1220 10 1 Robertson 34° 35' 150° 36' 720 13 Rossi 35° 29' 149° 30' 970-1070 16 Bad j a 36° 13' 149° 29' 1070 0 3 Bombala 37° 08' 149° 12' 910 13 1 Victoria Bendoe 37° 10' 148° 55' 1070 1 2 South Africa Draycott, Natal 29° 00' 29° 45' 1500 6 New Zealand Tairua 37° 09' 175° 50' 20 1 Cambridge 37° 53' 175° 29' 40 5 Ngahinapouri 37° 53' 175° 15' 40 1 Rotoehu 37° 56' 176° 35' 90 1 Tikitere 38° 04' 176° 22' 350 4 Rotorua 38° 09' 176° 15' 305 7 Waimana 38° 08' 177° 05' 30 1 Kaingaroa 38° 31' 176° 35' 460 4 1 Lake Mangamahoe 39° 07' 174° 07' 150 1 Oakura 39° 08' 173° 59' 125 11 1 Hunterville 39° 55' 175° 33' 300 9 Broughton Bay 41° 13' 173° 56' 20 1 Lake Ahaura 42° 33' 171° 44' 300 1 Heathcote 43° 35' 172° 42' 150 1 Charteris Bay 43° 40' 172° 43' 60 1 * Families are seedlots from single trees; composites are commercial seedlots from various numbers of trees. Test Sites and Establishment The details of the two test sites are as follows: Kinleith: Experiment No. R 1976; latitude 38° 17'S; longitude 176° OO'E; altitude 490 m; slope 3-14°; previous crop = Pinus radiata D. Don plantation; preparation = area logged 1978, topsoil heaped into ridges 3 m apart by tractor with V-blade; soil = loam overlying volcanic ash; air drainage = poor in places; location = Rauna Road, Cpt 691, N.Z. Forest Products Limited, Kinleith. Kaingaroa: Experiment No. R 1975; latitude 38° 27'S; longitude 176° 42'E; altitude 270m; slope 2-11°; previous crop =: Pinus ponderosa C Lawson plantation (1927); preparation := area logged 1978, burnt February 1979; soil = shallow layer Wilcox — Genetic variation in E. fastigata 513 148 150' 152° FIG. 1—Origins of eight native provenances (•) of Eucalyptus fastigata studied m New Zealand. of dark topsoil overlying coarse, yellow, rhyolite ash; air drainage — poor in places; location = Caves Road, Cpt 1207, Kaingaroa Forest, near Murupara. Trees were planted at 3 X 3 m spacing at Kinleith and 3 X 2.5 m at Kaingaroa, and 25 g of the slow-release fertiliser MagAmp(R) (registered trade mark of W. R. Grace 514 New Zealand Journal of Forestry Science 12(3) I ,— 1 1 1 ^ V?\ °§ /TAIRUA -36°sJ \M W / ROTORUA \2^Z IY I ,TIKITERE (5\J 4 II ROTOEHU \ ) / / / WAIMANA CAMBRIDGE . 1 r^v // / //V NGAHINAPOURI- KAINGAROA LAKE MANGAMAJ-IOE \S \^ ~ / \ OAKURA--^^^ 1 II INTTRVII 1 r BROUGHTON BAY--/J7 /? f / ^^r ^ / -4i°s-l LAKE AHAURA-^^/^N-^-^^ y L ^HEATHCOTE ^CHARTERIS BAY L f? -46°S-| t> SCALE 1:9 000 000 90 0 90 180 270 360 I 1 iiiil 1 KILOMETRES I 1 174°E 178°E I 170°E I —I I I FIG. 2—Localities of E. fastigata stands in New Zealand represented by seedlots m the breeding programme. Wilcox — Genetic variation in E. jastigata 515 & Co., United States) was incorporated in the planting hole. Hand weeding was carried out in January 1980. The Kinleith test was treated from the air with urea (250 kg/ha) in August 1980. The Kaingaroa test was treated with "Rustica" (NPK + MgO, 15 : 7 : 5 :4) at a rate of 78 g per tree applied in a circle round the tree, in April 1980, and with urea at a rate of 60 g per tree applied in a slit, in October 1980. Experimental Design The Kinleith site was divided into 108 sub-blocks of 18 X 21m. Sub-blocks were grouped in threes to make up 36 block replicates each of 0.113 ha. The Kaingaroa site was divided into 126 sub-blocks, 15 X 21m. Sub-blocks were grouped in threes to make up 42 block replicates of 0.094 ha. The 126 seedlots were divided into three sets of 42 in a way which gave more or less equal representation of provenances in each set. Sets were assigned randomly to one of the three sub-blocks in each block replicate at each site.
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